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HomeMy WebLinkAbout20090133 Ver 7_Year 3 Stream and Vegetation_20181228Stream and Vegetation Monitoring Year 3 Report UT to Stirrup Iron Creek / December 2018 / RAP -12020 'l WADAMS 'J MCADAMS UT TO STIRRUP IRON CREEK > MONITORING YEAR 3 REPORT Table of Contents 1.0 Introduction............................................................................................................................................2 1.1 Project Location and Description......................................................................................................2 1.2 Project Goals and Objectives............................................................................................................2 2.0 Channel Stability Assessment.................................................................................................................2 2.1 Visual Assessment Summary............................................................................................................3 3.0 Vegetation Condition and Comparison...................................................................................................4 3.1 Vegetation Monitoring Plots.............................................................................................................4 3.2 Vegetation Monitoring Plot Photos and Data Sheets.......................................................................4 4.0 References..............................................................................................................................................5 Appendix A: Site Maps Figure 1: Site Location Map Figure 2: Conservation Easement Map Appendix B: Vegetation Assessment Data Table 1: Vegetation Plot Mitigation Success Summary Table 2: Stem Count Total and Planted Species by Vegetation Plot Table 3: Planted Species Comparison by Vegetation Plot Appendix C: Vegetation Monitoring Plot Photos Appendix D: Vegetation Monitoring Plot Data Sheets creating experiences through experience 2905 Meridian Parkway, Durham, NC 27713 / 919. 361. 5000 'J MCADAMS UT TO STIRRUP IRON CREEK > MONITORING YEAR 3 REPORT 1.0 Introduction 1.1 Project Location and Description The UT to Stirrup Iron Creek Stream Restoration project (Stream Restoration project) is on the site of the Creekside at Bethpage residential development in Durham, Durham County, North Carolina (Appendix A, Figure 1). The project is located approximately 1.5 miles northwest of the intersection of Page Road and Chin Page Road. The constructed Stream Restoration project is part of the compensatory mitigation plan to offset stream and wetland impacts associated with the Creekside at Bethpage project. The Conservation Easement (CE) for the Stream Restoration project is 2.89 acres in size and is located within the west central portion of the overall project. The Stream Restoration project flows west and southwest and ties back in to another UT to Stirrup Iron Creek (Appendix A, Sheet No. 1-1). The restored stream length is 1,958 linear feet. The Stream Restoration project is approximately 0.25 miles from the proposed stream impacts associated with the Creekside at Bethpage residential development. The Stream Restoration project is located within the Neuse River Basin USGS Hydrologic Unit 03020201, local watershed 14 -digit basin 03020201080010 and the North Carolina Division of Water Resources (DWR) sub -basin 03-04-02. The unnamed tributary flows into Stirrup Iron Creek (DWR stream index number 27-33-4-2) approximately 1.0 mile downstream of the project terminus. 1.2 Project Goals and Objectives The purpose of this Stream and Vegetation Monitoring Year 3 Report is to assess the success of the Stream Restoration project. The monitoring plan evaluates the success of the Site and is based on the U.S. Army Corps of Engineers (USACE) "Stream Mitigation Guidelines" (April, 2013) and the North Carolina Ecosystem Enhancement Program (NCEEP) Monitoring Requirements and Performance Standards for Stream and/or Wetland Mitigation (November, 2011). Monitoring of the Site will occur annually for five (5) years. Construction of the Stream Restoration project occurred in the fall of 2015. During the month of November 2015, riparian buffer restoration activities began following construction of the restored active stream channel. Riparian buffer restoration activities included planting trees and staking vegetation plots within the CE. Baseline vegetation sampling was conducted on February 18, 2016. According to the Restoration Plan for the Stream Restoration project (issued July 2009), project specific goals and objectives related to vegetative assemblages within the stream restoration project were the following: > Ensure channel and stream bank stabilization by integrating native vegetation into the restoration design while also creating a stable and functional aquatic and terrestrial habitat. > Establish a native forested riparian plant community within a minimum of 50 feet from the proposed top of the bankfull channel, remove exotic vegetation during construction implementation and eliminate embankment maintenance practices. 2.0 Channel Stability Assessment Stream geometry will be considered successful if the geometry, profile and sinuosity are stable or reach a dynamic equilibrium. It is expected that there will be minimal changes in the designed cross sections, profile and substrate composition. Changes that may occur during the monitoring period will be evaluated to determine if they represent a movement toward a less stable condition (e.g. down cutting, or bank erosion) or are minor changes that represent an increase in stability (e.g. settling, vegetative changes, coarsening of bed material, etc.). Deviation creating experiences through experience 2 of 5 'J MCADAMS UT TO STIRRUP IRON CREEK > MONITORING YEAR 3 REPORT from the design ratios will not necessarily denote failure as it is possible to maintain stability and not stay within the design geometry. Channel stability will be reflected in the surveyed permanent cross-sections, longitudinal profile, evaluation of bank stability and cover and evaluation of in -stream structure performance compared to the as -built and any previously collected monitoring data. The general trend should reflect a stable or slightly decreasing riffle cross- sectional area, whereas pools may increase and yet be considered relatively stable. The longitudinal profile will typically adjust depending on the frequency of bankfull or greater storm events. Typically, the constructed channel profile will adjust (especially in a sand dominated bed), but it will need to function without significant degradation (bed scour), aggradation (mid -channel bars), or bank erosion. The Bank Height Ratio (BHR) shall not exceed 1.2 and the Entrenchment Ratio shall be no less than 2.2. The stream shall remain stable over five years and through two bankfull events, as indicated by visual surveys and monitoring of cross-sections and bank pins. 2.1 Visual Assessment Summary A visual assessment of the stream channel condition and stability was conducted by McAdams staff on September 25, 2018. Several areas of erosion and bank instability were noted in Monitoring Year 3. Moderate bank erosion and channel downcutting were observed throughout much of the reach. In general, the rock structures are performing well and remain stable. However, there is significant bank erosion at several of the log structures and on the outsides of some of the bends. In several cases, bank pins are exposed by a foot or more and the right bank near Vegetation Plot 3 has eroded to the extent that the end of a log vane is exposed and water is flowing around it. The observed bank erosion is evidence of lateral instability. A longitudinal profile will be surveyed to determine whether vertical instability is also an issue. While some lateral and vertical movement is expected, areas of observed instability in Monitoring Year 3 should be monitored and remedial actions may be necessary if the condition becomes severe. During Year 1 monitoring activities, excessive sediment loads were observed from the contributing watershed, likely from the construction activities associated with the Bethpage development. During Monitoring Year 3 activities, it was noted that the observed sediment load from the contributing watershed continues to pose a threat to water quality within and downstream of the restoration reach. In Monitoring Year 2, potential stability issues related to the outfall of a stormwater pond that was installed at the Bethpage site adjacent to the CE north of Vegetation Plot 3 were documented. During Year 2 monitoring activities, water with high levels of suspended sediment was observed discharging from this pond adjacent to the CE and pooling on the floodplain within the CE. In Monitoring Year 3 the water flowing out of the pond outlet was observed to have caused a small channel to form below the pond outlet. It is recommended that the outlet of the stormwater pond near Vegetation Plot 3 be evaluated for compliance with applicable stormwater regulations and that the area be monitored periodically to ensure that further stability issues do not develop in this area. Additionally, it is recommended that the Duke Power easement crossing, which was repaired in November 2016, continue be monitored for stability and that the sediment and erosion control measures on the Creekside at Bethpage construction site be monitored regularly to ensure that they remain in compliance with City of Durham regulations. Due to the potential channel and bank stability concerns observed during Year 3 monitoring, the cross sections and a longitudinal profile of the stream channel will be surveyed in early 2019 as part of the Year 3 monitoring activities. The cross section and longitudinal profile survey results will be submitted as soon as they can be completed. A stormwater and conservation easement compliance assessment focusing on the area of erosion creating experiences through experience 3 of 5 'J MCADAMS UT TO STIRRUP IRON CREEK > MONITORING YEAR 3 REPORT near the stormwater pond north of Vegetation Plot 3 will also be conducted at this time. The purpose of the assessment will be to determine whether compliance issues are contributing to the erosion problem in this area and to determine whether remedial action is required. 3.0 Vegetation Condition and Comparison The primary focus of the vegetative monitoring will be solely on the tree stratum, although shrub and herbaceous species encountered may also be recorded. Vegetation planting success criteria will be based on the survival of a minimum density of 320 trees per acre (to include both planted and existing trees) after three (3) years of monitoring. After five (5) years of monitoring, the density shall be no less than 260 trees per acre (to include both planted and existing trees). Vegetation plots will be sampled and reported in years 1, 2, 3, 4 and 5. Four (4) vegetative monitoring plots (Appendix A, Figure 2) were installed during As -Built monitoring. The vegetation monitoring plots were installed randomly throughout the Stream Restoration project. Because many canopy trees within the easement were preserved during construction, the planted area is largely limited to narrow areas along the stream banks. This limited planting area made it difficult to establish 100 -square -meter vegetation plots; thus, the plots vary in size from 31.0 to 96.5 square meters. All four (4) corners of the vegetation monitoring plots were permanently installed and surveyed. Baseline vegetation monitoring was conducted in general accordance with CVS-EEP Protocol for Recording Vegetation (CVS-EEP, v4.2) as a basis for subsequent vegetation monitoring activities and reports. 3.1 Vegetation Monitoring Plots Monitoring Year 3 field activities were conducted September 25, 2018. Monitoring methodologies followed the most current templates and guidelines provided by EEP (EEP 2004; EEP 2011). All four (4) vegetation monitoring plots installed by McAdams were located in Monitoring Year 3. Figure 2 (Appendix A) depicts the location of the vegetation monitoring plots. Plant species, density, survival rates and the cause of mortality, if identifiable, were recorded within each vegetation monitoring plot. Table 1 (Appendix B) provides a success summary for each vegetation monitoring plot. In Monitoring Year 3, the Stream Restoration project had four (4) vegetation monitoring plots encompassing 0.07 acres, containing 51 planted stems, which yielded a density of 729 planted stems per acre. All four (4) vegetation monitoring plots met the interim vegetation monitoring criteria with a range of 410 to 1,123 stems per acre. Table 2 (Appendix B) provides a stem count total and planted stem total by each individual vegetation plot. Table 3 (Appendix B) provides a summary of only planted stem counts as compared to planted stem counts of the As -Built. 3.2 Vegetation Monitoring Plot Photos and Data Sheets Photographs of the vegetation monitoring plots are provided in Appendix C. Vegetation Monitoring Plot Data Sheets are provided in Appendix D. Each Vegetation Monitoring Plot Data Sheet provides measurements, location, and vigor of each planted species within a respective vegetation monitoring plot. creating experiences through experience 4 of 5 'J MCADAMS UT TO STIRRUP IRON CREEK > MONITORING YEAR 3 REPORT 4.0 References Lee Michael T., Peet Robert K., Roberts Steven D., and Wentworth Thomas R., 2008. CVS-EEP Protocol for Recording Vegetation Level. Version 4.2. North Carolina Ecosystem Enhancement Program (NCEEP) 2004. Guidelines for Riparian Buffer Restoration. Available at internet site: https://erp.unc.edu/files/2014/12/buffer-restoration.pdf. North Carolina Ecosystem Enhancement Program (NCEEP) November 7, 2011. Monitoring Requirements and Performance Standards for Stream and/or Wetland Mitigation. Schafale MP and AS Weakley. 1990. Classification of the Natural Communities of North Carolina: Third Approximation. North Carolina Natural Heritage Program, Division of Parks and Recreation, Department of Environment and Natural Resources. Raleigh, North Carolina. The John R. McAdams Company, Inc. July 2016. As -Built Monitoring Report, UT to Stirrup Iron Creek. US Army Corps of Engineers April, 2013. Stream Mitigation Guidelines. creating experiences through experience 5 of 5 'J MCADAMS UT TO STIRRUP IRON CREEK > MONITORING YEAR 3 REPORT APPENDIX A Site Maps creating experiences through experience .r + J\a 1 �•;! tl J i �s'` _ � � " t, sem_ � •.r .; � i• � / } BETHP AGE DEVELOPMEN r` 1. _ r v ---�y f- 1 LEI 7.k r' i +� f� _ C� : • - ,-� .L. �f' •�`� 1 . � � � `� ` • 4 � R. J��` -� ; ,moi � � fgTXFZT ._ �m 4Y � _.�• - c�,'f� % , '-fit - n �', . sY ?8M ? J Ar / l d ..� i. USGS - SOUTH EAST DURHAM QUAD LAT / LONG LOCATION: 35.9024310° N 178.8318007' W CHIN nu AIRPORT VICINITY MAP NTS Ve PRaecr No. CPR -08000 VICINITY MAP EcoEngineering FILENAME. CPRO800OX�j (�g T�TT R �jA I RE I division of1La John R McAdams Compacry, Fmc.1 SCAi,E: 1 ^ a 2,000• V UT to STIRRUP IRON CREEK RESEARCH TR[ANGLE PARK, NC P.O. Box «0052[P 27709 4005 °AT9: 7--9-2009 DURHAM, NORTH CAROLINA (919) 88i-5000 USGS - SOUTH EAST DURHAM QUAD LAT / LONG LOCATION: 35.9024310° N 178.8318007' W CHIN nu AIRPORT VICINITY MAP NTS PRaecr No. CPR -08000 VICINITY MAP EcoEngineering FILENAME. CPRO800OX�j (�g T�TT R �jA I RE I division of1La John R McAdams Compacry, Fmc.1 SCAi,E: 1 ^ a 2,000• V UT to STIRRUP IRON CREEK RESEARCH TR[ANGLE PARK, NC P.O. Box «0052[P 27709 4005 °AT9: 7--9-2009 DURHAM, NORTH CAROLINA (919) 88i-5000 'J MCADAMS UT TO STIRRUP IRON CREEK > MONITORING YEAR 3 REPORT re1»40111kyll Vegetation Assessment Data creating experiences through experience Table 1. Vegetation Plot Mitigation Success Summary Table UT to Stirrup Iron Creek Stream Restoration Site Durham, NC VEGETATION MONITORING YEAR 3: September 25, 2018 McAdams Project #: RAP -12020 Vegetation Plot ID Vegetation Threshold Met?* Tract Mean 1 Yes 100% 2 Yes 3 Yes 4 Yes *Tree survival should consist of at least 320 trees per acre (including both planted and existing trees) for the first 3 years after construction and at least 260 trees per acre after 5 years, according to the "UT to Stirrup Iron Creek Stream and Vegetation Monitoring Plan" (June 2018). Table 2. Planted Stem Count Total by Vegation Plot UT to Stirrup Iron Creek Stream Restoration Site Durham, NC VEGETATION MONITORING YEAR 3: September 25, 2018 McAdams Project #: RAP -12020 Scientific Name Common Name Species Type MY3 ANNUAL TOTALS VP -1 I VP -2 VP -3 I VP -4 JMY3 (SEPT 2018) MY2 (DEC 2017) 1 MY1 (OCT 2016) AS -BUILT (FEB 2016 Planted Stems Carpinus caroliniana American hornbeam tree 0 0 2 3 Cephalanthus occidentalis button bush shrub 3 1 5 9 0 0 0 Fraxinus pennsylvanica green ash tree 3 7 10 9 12 9 Liriodendron tulipifera tulip poplar tree 14 2 16 5 9 26 Myrica cerifera wax myrtle shrub 2 1 3 4 3 7 Nyssa bii lora swamp tupelo tree 0 1 2 2 Persea palustris swamp bay small tree 1 1 6 5 11 Platanus occidentalis sycamore tree 1 1 0 0 0 Quercus laurifolia laurel oak tree 0 1 2 34 Quercus michauxii swamp chestnut oak tree 1 1 2 0 0 1 Quercus nigra water oak tree 2 1 2 3 3 0 Quercus phellos willow oak tree 1 1 2 0 0 Quercus sp. oak species tree 3 1 1 5 9 0 0 Ulmus americana American elm tree 1 1 6 6 20 Vaccinium corymbosum blueberry shrub 0 0 1 8 Stem Count Total 24 15 5 1 7 51 46 47 121 Size of Vegetation Plot (Acres) 0.02 0.02 0.01 0.02 0.07 0.07 0.07 0.07 Number of Different Species 7 5 4 3 11 10 10 10 Stems Per Acre 1123 629 653 410 729 658 672 1730 Total CE Area = 2.89 acres Table 3. Planted Species Mortality by Vegation Plot UT to Stirrup Iron Creek Stream Restoration Site Durham, NC VEGETATION MONITORING YEAR 3: September 25, 2018 McAdams Project #: RAP -12020 Note: Reductions in the number of planted stems are due to species which were deemed "missing" or "dead" at the time of monitoring. One possible explanation for "missing" species is due to thick herbaceous growth obscurring the species from identification. Increases in the number of planted stems may be due to stems that were previously noted as "missing" but are found in subsequent monitoring years, survival of stems which were previously deemed "dead" but were dormant at the time of monitoring and put out new growth in the current monitoring year or the addition of newly identified volunteer stems. VP -1 VP -2 VP -3 VP -4 Monitoring Year 3 Planted Stem Count Total 24 15 5 7 Monitoring Year 2 Planted Stem Count Total 15 14 7 10 Planted Stem Difference from MY2 9 1 -2 -3 Mortality Rate (%) -60% -7% 29% 30% Note: Reductions in the number of planted stems are due to species which were deemed "missing" or "dead" at the time of monitoring. One possible explanation for "missing" species is due to thick herbaceous growth obscurring the species from identification. Increases in the number of planted stems may be due to stems that were previously noted as "missing" but are found in subsequent monitoring years, survival of stems which were previously deemed "dead" but were dormant at the time of monitoring and put out new growth in the current monitoring year or the addition of newly identified volunteer stems. 'J MCADAMS UT TO STIRRUP IRON CREEK > MONITORING YEAR 3 REPORT APPENDIX C Vegetation Monitoring Plot Photos creating experiences through experience 'J MCADAMS UT TO STIRRUP IRON CREEK > MONITORING YEAR 3 REPORT Vegetation Plot 3: View facing 250°W Vegetation Plot 4: View facing 30°N creating experiences through experience 2 of 2 'J MCADAMS UT TO STIRRUP IRON CREEK > MONITORING YEAR 3 REPORT lel» 4►111 EIvf . Vegetation Monitoring Plot Data Sheets creating experiences through experience Site: Bethpage Page: 1 Monitoring Year: MY3 Date: 9/25/2018 Area: 9.2 x 9.4 Veg Plot No.: 1 X-axis: Plot Location: 120°ECURRENT see sketch below X Y ddh YEAR DATA Height DBH Map ID Scientific Name Source meter meter mm cm cm Vigor Notes 1 Quercus s. B 1.8 1.2 5 45 3 2 Liriodendron tuli ifera B 3.1 1.1 130 0.5 3 3 Liriodendron tuli ifera* B 7.3 0.8 12 114 3 4 Ulmus americana B 8.6 0.7 Missing 5 Liriodendron tuli ifera* B 1 8.2 1.61 7 77 3 61 Quercus sp. B 6.1 2.1 Missing 7 Fraxinus enns Ivanica* B 6.9 1.7 14 118 3 8 Quercus sp. B 3.3 2.9 Missing 9 Liriodendron tuli ifera B 4.1 3.5 6 56 3 10 Vaccinium cor mbosom B 1.8 2.8 Missin 11 Liriodendron tuli ifera* B 0.3 2.8 5 52 3 12 Quercus sp. B 1.5 4.3 Missing 13 Quercus sp. B 4.5 4.5 Dead 14 Fraxinus pennsylvanica B 7.8 4.4 Missing 15 Ulmus americana B 8.7 4.0 Missing 16 Liriodendron tuli ifera* B 8.3 5.7 10 104 3 17 Liriodendron tuli ifera B 7.3 6.0 127 0.5 3 18 Liriodendron tuli ifera* B 7.1 7.1 Missing 19 Liriodendron tuli ifera B 7.1 7.11 11 105 3 20 Fraxinus pennsylvanica B 6.6 6.8 129 0.5 3 21 Quercus sp. B 6.6 7.7 Missing 22 Liriodendron tuli ifera B 4.7 6.1 12 114 3 23 Liriodendron tuli ifera B 3.3 6.7 7 73 3 24 Quercus phellos B 3.6 6.0 4 44 3 Res rout 25 Liriodendron tuli ifera B 2.5 5.0 6 77 3 26 Quercus sp. B 1.6 4.41 Missing 27 Ulmus americana B 0.1 5.8 Missing 28 Quercus sp. B 0.1 7.4 Missing 29 Liriodendron tuli ifera* B 1.7 9.1 6 79 3 30 Fraxinus pennsylvanica B 2.4 7.6 5 50 3 31 Quercus sp. B 2.8 8.4 8 60 3 32 Quercus sp. B 4.3 8.4 7 60 2 Die back 33 Quercus michauxii* B 5.1 9.4 7 22 3 Die back 34 Liriodendron tuli ifera B 6.5 9.3 6 51 3 351 Platanus occidentalis* B 6.5 7.8 5 87 3 361 Ulmus americana* B 7.8 8.2 8 91 3 37 1 Liriodendron tuli ifera B 7.9 8.4 71 85 3 B = bare root *Species identified differently in MY3 than in MY2 C= containerized Volunteer Species Height Class cm Scientific Name 10-50 50-100 >100 Li uidambar st raciflua 2 Liriodendron tuli ifera 10 20 Platanus occidentalis 2 2 Rhus co allinum 2 Cornus sip. 1 Tree line Y (0, 9.4) (0,0) X (9.2, 0) Tree line Site: Bethpage Page: 2 Monitoring Year: MY3 Date: 9/25/2018 Area: 9.2 x 9.4 Veg Plot No.: 1 X-axis: 1201E A 9.0 8.0 7.0 6.0 5.0 4.0 3.0 2.0 1.0 0.0 i 0 1 2 3 4 5 6 7 8 9 O Fraxinus pennsylvanica O Liriodendron tulipifera O Platanus occidentalis 0 Quercus michauxii 0 Quercus phellos 0 Quercus sp. 0 Ulmus americana 0 Vaccinium corymbosom 0 Missing x Dead 33 34 ------------------- ------- -- ------- -------- ------- ---------------- ------------ 36 -------------- -- D--4 - - - - - - - - 8 - - - - - - - - - : -------- - - - - -0------ - - - - - - - - - - ------- - --------- - - - - - - --------- - - - - - - ------ - - - - - - - - - - - - - - - - - - - - - - - - - - - -------- - - ---------------- -------- ------- t ----------- 0- ---------------- ---------------- ------- -------- -------- -------- -------- ------- ----------- ---------------- ---------------- 9 ---------------- 217 ---------------- ------- -------- -------- 16 ---------- -- ------- ---- -0 -------------- - ----------------------------- -------- 14 -------- -- ------------- 25 ------- ------------ 15 ---------------- -------------------- ------------ ------- ------- -------- ------- -------- -------- -------- -------- ------- -------- -- 11 --------------10 -------- ----------- - - ------ -------------- ------- -------- -- 66 ---------------- ---------------- ------------------------ ----------------- ------------ 71 C ........ ........ . 0 102- ---------------- ---------------- ---------------------------------- I ---------------- ------- -------- -------- -------- -------- ------ ------ 0.0 i 0 1 2 3 4 5 6 7 8 9 O Fraxinus pennsylvanica O Liriodendron tulipifera O Platanus occidentalis 0 Quercus michauxii 0 Quercus phellos 0 Quercus sp. 0 Ulmus americana 0 Vaccinium corymbosom 0 Missing x Dead Site: Bethpage Page: 1 Monitoring Year: MY3 Date: 9/25/2018 Area: 20.1 x 4.8 Veg Plot No.: 2 X-axis: Plot Location: 345°N see sketch below Map ID Scientific Name X I Y Source meter meter ddh mm CURRENT YEAR DATA Height DBH cm cm Vigor Notes 1 Fraxinus pennsylvanica B 0.9 0.1 9 83 Fraxinus pennsylvanica 3 2 Fraxinus pennsylvanica B 0.6 1.6 9 50 3 3 Cephalanthus occidentalis* B 0.9 3.0 6 78 3 4 Fraxinus pennsylvanica B 0.8 3.7 10 80 3 5 Quercus nigra* B 1.4 4.41 5 46 3 61 Ulmus americana B 1.41 1.31 Dead 7 Liriodendron tulipifera B 4.3 0.5 6 46 3 8 Liriodendron tulipifera B 3.5 1.2 Missing 9 Quercus nigra B 3.7 2.7 Missing 10 Quercus nigra B 4.3 2.1 5 60 3 11 Fraxinus pennsylvanica B 5.7 0.8 7 47 3 12 Liriodendron tulipifera B 6.0 1.3 Dead 13 Quercus sp. B 6.2 3.0 Dead 14 Quercus sp. B 7.3 4.6 Dead 15 Fraxinus pennsylvanica B 8.1 0.7 5 41 3 16 Liriodendron tulipifera B 8.0 1.9 Missing 17 Liriodendron tulipifera B 8.4 2.6 Missing 18 Cephalanthus occidentalis* B 8.8 4.8 230 1.3 3 19 Liriodendron tulipifera B 8.91 0.4 Missing 20 1 Fraxinus pennsylvanica B 10.8 0.9 11 82 3 21 Liriodendron tulipifera B 10.2 2.5 Dead 22 Vaccinium corymbosum B 10.8 4.5 Missing 23 Ulmus americana B 12.6 4.1 Missing 24 Liriodendron tulipifera* B 13.0 2.61 5 51 3 Deer 25 Fraxinus pennsylvanica B 13.0 0.7 161 0.9 3 26 Cephalanthus occidentalis* B 14.4 3.1 245 1.5 3 27 Quercus sp. B 17.2 2.51 7 651 3 281 Ulmus americana B 18.3 3.71 1 Missing B = bare root *Species identified differently in MY3 than in MY2 C= containerized SS Y (0, 4.8) 4.8) (0,0) X (20.1,0) Volunteer Species Height Class (cm) Scientific Name 10-50 50-100 >100 Salix nigra 2 Platanus occidentalis 1 1 Liriodendron tulipifera 10 2 Fraxinus pennsylvanica 1 Site: Bethpage Page: 2 Monitoring Year: MY3 Date: 9/25/2018 Area: 20.1 x 4.8 Veg Plot No.: 2 X-axis: 3451N - - - - - - - - - - - - - - - - - - - - - - - - - - - - ----- - - - - - - - - - - - - - - - - - - --- - I - - - - - - --- - TIT, - - - - - - - - - - - -- - - - - - -- - r ---- - ---------- 3 ---------a3 :G I ----------- ---- ----- ---- ---- -- ---- I ------ ---- ---------- ---- ------ I ---- ---- I ------ ---- I ----- ------ I ---- ---- I ------ ---- ------------------------- - (,J) -- ---- c --------- ---------- ---- ----- ----- ----- ---------- ---- --------- ---------- ---- ----- 10� - -- ---------------- ----- F ---- ---- ------ ---------- ----- F ---- ----------- - - 015 ----- ----- ---- ---- 4- 5 ----- -- ---------- ---- --- 0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 0 Cephalanthus occidentalis 0 Fraxinus pennsylvanka 0 Liriodendron tulipifera 0 Quercus nigra 0 Quercus sp. 0 Ulmus americana 0 Vaccinium corymbosum 0 Missing x Dead Site: Bethpage Page: 1 Monitoring Year: MY3 Date: 9/25/2018 Area: 15.5 x 2.0 Veg Plot No.: 3 X-axis: Plot Location: 250°WCURRENT see sketch below Map ID Scientific Name X Y Source meter meter ddh mm YEAR DATA Height DBH cm cm Vigor Notes 1 Ulmus americana B 0.4 1.7 Missing 2 Cephalanthus occidentalis* B 1.5 0.5 7 83 3 3 Persea palustris B 2.0 0.9 Missing 4 Myrica cerifera B 2.5 0.7 11 121 3 5 Vaccinium corymbosum B 2.91 1.51 1 Missing 61 Liriodendron tulipifera B 3.2 1.1 Missing 7 Quercus michauxii* B 4.5 0.5 3 27 3 8 Myrica cerifera B 5.7 1.3 Missing 9 Liriodendron tulipifera B 5.7 1.1 Missing 10 Vaccinium corymbosum B 6.3 1.6 Missing 11 Persea palustris B 7.0 1.4 Missing 12 Liriodendron tulipifera B 8.01 0.71 1 lMissing 131 Quercus laurifolia* B 9.3 1.1 Missing 14 Quercus sp.* B 9.5 0.9 7 51 3 15 Persea palustris B 9.6 0.9 Missing 16 Ulmus americana B 10.1 0.8 Missing 17 Myrica cerifera B 12.6 1.8 137 0.3 3 18 Liriodendron tulipifera IB 1 12.3 0.6 Missing 19 Persea palustris I B 13.31 1.91 1Missin 20 Liriodendron tulipifera IB 14.41 1.51 Imissing 211 Quercus sp. IB 1 15.41 1.91 1 1 IMissing 0) B = bare root *Species identified differently in MY2 than during As -built and/or MY1 monitoring C= containerized Stream ■ ■ ■ ■ (0,0) X (15.5, 0). ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ ■ Tree line *Water from SCM outlet pipe is sediment laden. Volunteer Species Height Class cm Scientific Name 10-50 150-1001 >100 Liriodendron tulipifera 1 21 1 Site: Bethpage Page: 2 Monitoring Year: MY3 Date: 9/25/2018 Area: 15.5 x 2.0 Veg Plot No.: 3 X-axis: 250OW 250'W ---------- ----------- ----- --- ------ ----- ----- 9 10 ---------------------------- ----------- ------------------------- 0 ----- 19: UU9. -- ---------- ---------- 0 --- ---0 I- ----- ------ -------- ------w 1-----v---- -- ----G —- ------------------ ---------- 0-: 0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 • Cepholanthus occidentalis 0 Liriodendron tulipifera 0 Myrica cerifera 0 Quercus lourifolia 0 Quercus michauxii 0 Quercus sp. • Vaccinium corymbosum 0 Missing 0 Quercus sp. 0 Persea palustris 0 Ulmus americana 250'W Site: Bethpage Page: 1 Monitoring Year: MY3 Date: 9/25/2018 Area: 19.2 x 3.6 Veg Plot No.: 4 X-axis: Plot Location: 30°NCURRENT see sketch below Map ID Scientific Name X Y Source meter meter YEAR DATA ddh Height DBH mm cm cm Vigor Notes 1 N ssa biflora B 0.2 1.5 Missing 2 Persea palustris B 0.5 1.7 Missing 3 Quercus laurifolia B 0.4 2.2 Missing 4 Quercus sp. B 1.1 1.6 Missing 5 N ssa biflora B 2.11 1.11 1 Missing 61 Cephalanthus occidentalis B 2.8 1.5 171 0.6 3 7 Fraxinus pennsylvanica B 2.8 2.2 Missing 8 Persea palustris B 3.4 2.3 6 76 3 9 Ulmus americana B 3.8 1.7 Missing 10 Myrica cerifera B 4.7 2.6 165 0.4 3 11 Liriodendron tuli ifera B 6.5 2.0 Missing 12 Carpinus caroliniana B 6.71 1.51 Missing 131 Cephalanthus occidentalis" B 6.7 0.3 300 1.9 3 14 Carpinus caroliniana B 7.5 1.0 Missing 15 Persea palustris B 6.9 2.6 Missing 16 Myrica cerifera B 7.7 3.0 Missing 17 Cephalanthus occidentalis" B 8.2 2.4 320 1.4 3 18 Vaccinium corymbosum B 7.9 2.1 Missing 19 Quercus sp. B 8.41 1.51 Missing 201 Carpinus caroliniana B 8.9 1.1 iMissing 21 Cephalanthus occidentalis" B 9.2 0.4 250 0.7 3 22 Ulmus americana B 10.3 1.7 Missing 23 Persea palustris B 10.6 1.4 Missing 24 Cephalanthus occidentalis' B 10.8 0.6 230 0.6 3 25 Vaccinium corymbosurn B 11.5 1.3 Missing 26 Quercus sp. B 11.81 1.91 Missing 271 Myrica cerifera B 11.4 2.0 iMissing 281 Ulmus americana B 11.0 2.3 Missing 29 Persea palustris B 13.0 3.5 Missing 30 Persea palustris B 13.4 2.2 Missing 31 Vaccinium corymbosurn B 13.1 1.9 Missing 32 Liriodendron tulipifera B 12.9 1.2 Missing 33 Liriodendron tuli ifera B 14.81 1.51 Missing 34 Myrica cerifera B 1 14.41 2.61 1 iMissing 351 Liriodendron tuli ifera B 1 16.91 2.21 1 1 1 IMissing B = bare root "Species identified differently in MY2 than during As -built and/or MY1 monitoring C= containerized XS 8 i Strew ltees.is Y (0, (0,0) I X (19.2, 0) ■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■■ Volunteer Species Hei ht Class jcmj Tree line Scientific Name 10-50 50-100 >100 Pinus 3 Salix nigra 4 Liriodendron tuli ifera 1 Site: Bethpage Page: 2 Monitoring Year: MY3 Date: 9/25/2018 Area: 19.2 x 3.6 Veg Plot No.: 4 X-axis: WIN mmmmmm mmmmm2mmmmmml 0 0 Fall 0 1 U.S. I c IS I . 1COD MIMMI MONOMER BE MEMEMMI 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 • Carpinus caroliniona Cepholanthus occidentalis 0 Fraxinus pennsylvanica 0 Liriodendron tulipifera • Myrica cerifera 0 Quercus sp. 0 Vaccinium corymbosum 0 Missing • Persea palustris 0 Nyssa biflora 0 Quercus laurifolia 0 Ulmus americana 30'N